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EXHIBITA— PAGE A4 <br /> Each of these factors and others combine to limit what type of compost facility is <br /> appropriate for a given location. For example, open windrows, with spacing in <br /> between, have lower cost of operation but require turning at least three times <br /> during active composting and this releases odor from the piles. The windrow <br /> piles consume comparatively more space on the property. If the selected site is <br /> distant from receptors and has enough room, this is a desirable choice. If, <br /> however, there are residents nearby who are concerned about odors, and the <br /> available space for composting is small, use of forced aeration under the pile is a <br /> better option to avoid turning the pile during active composting. This approach <br /> allows them to be constructed with no space in between. Under either approach <br /> seasonal volumes fluctuate, and this must be considered as a space <br /> consideration, as most yard waste for composting is generated during late spring, <br /> summer, and early fall. Another example is the selection of equipment. On the <br /> front end, if the goal is to grind yard waste and mix it with food scrap, the <br /> amount of each material dictates the size and type needed to accomplish this. <br /> On the back end, if the goal is to use sediments and create a topsoil mix from the <br /> finished compost, the proper equipment selection and storage becomes <br /> important. <br /> These examples show that there is no one-size-fits-all approach to the design of <br /> an organic material composting facility. The conceptual design will take these and <br /> other factors into account to meet the vision and mission statement of the Plan, <br /> while taking into consideration the identified financial constraints that must be <br /> considered to operate in a sustainable fashion. <br /> 5. Evaluation of windrow design vs. a mechanical aerobic or anaerobic digestion <br /> system <br /> As identified above for the conceptual design, the evaluation of various specific <br /> organic material processes will depend on environmental and economic factors <br /> that either support or reject the use of one technology over the other. The type <br /> and availability of different feedstocks might favor one over the other. For <br /> example, a process exists to convert high moisture food scrap into a liquid soil <br /> nutrient (Terreplenish) that can create a separate added value product for sale at <br /> the facility, in addition to finished compost. As the compost process becomes <br /> more complex the upfront capital cost increases, and financing can become an <br /> issue. The JPLEE team will summarize the advantages and disadvantages of using <br /> one technology over another, factoring in the amount and types of waste <br /> identified in the Plan, the commitments of stakeholders and regulatory barriers. <br /> 6. Estimates of compost production <br /> The amount of compost production will be calculated by the JPLEE team using <br /> the identified amount and type of reliable feedstock as input, and the processing <br /> capacity imposed by the selected compost location, equipment, and technology <br /> 3 <br />